Continuing Fire Regimes in Remote Forests of Grand Canyon National Park
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Continuing Fire Regimes in Remote Forests of Grand Canyon National Park Peter Z. Fulé Thomas A. Heinlein W. Wallace Covington Margaret M. Moore Abstract—Ponderosa pine forests in which frequent fire regimes Kaibab Plateau. It took another 78 years before the first continue up to the present would be invaluable points of reference European settlement was begun by Mormon explorers and for assessing natural ecological attributes. A few remote forests on pioneers in 1854. Fighting with Utes and Navajos kept the North Rim of Grand Canyon National Park come close to this settlers out of the Arizona Strip until 1869. With the ideal: never-harvested, distant from human communities and fire establishment of peace, there was a rapid expansion of suppression resources, and with several low-intensity fires in the livestock grazing, logging and mining activity. past century—a highly unusual recent fire regime in the Southwest. Frequent fire regimes were disrupted in forested high- Recent fires appear to have played a crucial role in preventing the lands of the Arizona Strip as early as 1870 in the Mt increases in forest density that characterize most southwestern Trumbull area (Fulé and others, unpublished data). As pine forests. The study sites are not unaffected by the ecological elsewhere in the Southwest, early livestock grazing was changes associated with settlement, but they do present an impor- excessive (Altshul and Fairley 1989) and removed fine tant reference resource for study and management of ponderosa herbaceous fuels, stopping fire spread. The establishment pine ecosystems. of the Grand Canyon Forest Reserve in 1893 and creation of Grand Canyon National Park (GCNP) in 1919 brought organized fire detection and suppression crews. On the North Rim, Wolf and Mast (1998) found complete fire Ponderosa pine forests in which historically frequent fire exclusion by about 1920 in ponderosa pine and mixed regimes continue up to the present would be invaluable conifer forests. Even in the high-elevation spruce-fir for- points of reference for assessing natural attributes of eco- ests, with historically longer fire-return intervals and more logical structure and function. Grand Canyon National Park severe fires, protracted fire exclusion has led to the devel- contains one of the largest old-growth forests in the South- opment of increasingly dense, homogeneous stands (White west, where tree harvesting has not occurred and grazing and Vankat 1993). Park management policy has changed has been eliminated for over 60 years. Although most fire in recent decades to favor restoration of natural ecological disturbance regimes in the park have been disrupted since processes, including fire (GCNP 1992), but the presently European settlement, a few remote sites may retain near- dense forests and heavy fuel loads hinder effective re- natural conditions. The majority of the forested area lies on introduction of fire on much of the North Rim. Fuel prob- the North Rim, part of the Kaibab Plateau, which supports lems are not only an ecological concern: the difficulty of fire ponderosa pine, mixed conifer and spruce-fir forests at management on the North Rim has been cited by Pyne elevations ranging from 7,500 to 9,165 feet on well-drained (1989) as a major factor impeding the Park’s plan for limestone soils. wilderness designation of the area (Morehouse 1996). The North Rim is remote from modern human communi- Among the challenges faced by managers are: 1) lack of ties, but Altshul and Fairley (1989) document the long knowledge about natural ecological conditions as a point of human history of the region. The lower elevations of the reference for restorative management (Moore and others rim were densely populated by Native Americans prior to 1999), 2) uncertainty about the appropriate mix of pre- 1250-1300 A.D. Six tribes—the Paiute, Hopi, Havasupai, scribed fire and tree thinning for treating accumulated Hualapai, Navajo, and Zuni—have ancestral and current fuels (Nichols and others 1994), and 3) a host of off-site connections to the canyon and rim habitat. An expedition issues including air quality, developing management pro- led by the Spaniards Dominguez and Escalante in 1776 cedures suitable for wilderness areas and working in a marked the first European presence on the Arizona Strip, highly charged political environment. the land north of the Colorado River that includes the Our study focuses on the first of these questions: charac- terizing fire regimes on several sites that may be among the least impacted by recent fire exclusion in the Southwest. The northwestern points and plateaus of the North Rim In: Cole, David N.; McCool, Stephen F.; Borrie, William T.; O’Loughlin, Jennifer, comps. 2000. Wilderness science in a time of change conference— have the most frequent lightning ignitions in the Park Volume 5: Wilderness ecosystems, threats, and management; 1999 May 23– (GCNP fire records). As part of a broader study on fire and 27; Missoula, MT. Proceedings RMRS-P-15-VOL-5. Ogden, UT: U.S. Depart- ment of Agriculture, Forest Service, Rocky Mountain Research Station. forest structure in the Park, we selected three representa- Peter Z. Fulé is Assistant Research Professor, Thomas A. Heinlein is tive sites: Powell Plateau, a mesa separated from the Research Specialist, W. Wallace Covington is Regents’ Professor, and Marga- Kaibab Plateau “mainland,” Fire Point, the westernmost ret M. Moore is Professor, School of Forestry, Northern Arizona Universiy, Flagstaff, AZ 86011 U.S.A. extension of the rim, and Rainbow Plateau, a peninsula to 242 USDA Forest Service Proceedings RMRS-P-15-VOL-5. 2000 the southeast (fig. 1). The forests are dominated by old average January minimum of 30° F (GCNP1992; White trees, with lush understory vegetation and substantial and Vankat 1993). Vegetation includes ponderosa pine evidence of recent fires. The sites are not without recent (Pinus ponderosa), Gambel oak (Quercus gambelli), and human impact: these areas were grazed prior to construc- New Mexican locust (Robinia neomexicana) trees, with an tion of the North Rim boundary fence in 1938 (Schroeder, understory of forbs and perennial grasses (Bennett 1974). personal commnication) and fire suppression was practiced Fire-scarred tree sampling was done in June-July, 1998. here through much of the 20th century (Pyne 1989). How- Partial cross-sections were cut from scarred “catfaces” on ever, we anticipated that the limited water for livestock and trees, logs, and stumps of conifers that appeared to repre- difficult access for firefighters might have minimized dis- sent the oldest and/or most extensive fire records. Samples ruption of the fire regime. Our goals were to quantify the fire were mapped when collected and were well-distributed regime, describe any post-settlement changes and assess throughout the study areas. In the lab, samples were management implications. mounted, surfaced with progressively finer sandpaper and crossdated (Stokes and Smiley 1968) using characteristic patterns of narrow marker years: 1722, 29, 35, 48, 52, 72, 82 Methods _______________________ (false ring), 1810, 13, 20, 22, 45, 47, 73, 79, 96, 99, 1902, 04, 51, 63, 77, 96. All dates were independently confirmed by The study sites totaled nearly 1,700 acres. The Powell another dendrochronologist. The season of fire occurrence Plateau site covered 780 acres, ranging from 7,400 to 7,660 (Baisan and Swetnam 1990) was estimated from the relative feet in elevation. The Fire Point site was 333 acres, 7,570 to position of each fire lesion within the annual ring. 7,770 feet in elevation. The Rainbow Plateau site was 550 Fire history data were analyzed with the FHX2 software acres, 7,550 to 7,658 feet in elevation. Soils have not been (Grissino-Mayer 1995). Analysis at each site began with the mapped in detail for these sites, but North Rim soils in first year with an adequate sample depth (Grissino-Mayer general are predominantly of the Soldier series, derived and others 1994). Fire return intervals were analyzed statis- from Kaibab limestone. Average annual precipitation on the tically in different categories related to the size and/or North Rim is 23 inches, with an average annual snowfall of intensity of past fires. The fire data were filtered to look at 129 inches. Temperatures are cooler than on the South Rim, progressively greater proportional scarring as a proxy for ranging from an average July maximum of 79° F to an Figure 1—Study sites on the North Rim of Grand Canyon National Park. USDA Forest Service Proceedings RMRS-P-15-VOL-5. 2000 243 fire size (Swetnam and Baisan 1996). First, all fire years, even America, we usually find sites with good records but no fires those represented by a single scar, were considered. Then, we (USA—Swetnam and Baisan 1996) or many fires but limited included only those fire years in which 10% or more, and 25% records (Mexico—Fulé and Covington 1997, 1999). The Grand or more, of the recording samples were scarred. The statisti- Canyon sites in the present study have both recent fires and cal analysis of fire return intervals includes several measures written historical data: fire records maintained at GCNP of central tendency: the mean fire interval (MFI, average since 1924 provide an unusual opportunity for a quantita- number of years between fires), the median and the Weibull tive test of the utility of fire scars in reconstructing the median probability interval (WMPI). temporal and spatial pattern of past fires. The relationship between climatic fluctuations and fire The fire record data were used with caution. The database occurrence was compared by superposed epoch analysis was patchy in the early years. Many recorded fire sizes and (SEA), using software developed by Grissino-Mayer (1995). geographic locations were considered approximate, and some A locally developed, ponderosa pine tree-ring chronology evident errors were observed, such as coordinates that served as a proxy for climate.